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Biologia, Bratislava, 62/4: 482—487, 2007 Section Zoology DOI: 10.2478/s11756-007-0092-6 Microhabitat use, seasonal activity and diet of the snake-eyed skink (Ablepharus kitaibelii fitzingeri)incomparison with sympatric lacertids in Hungary Gábor Herczeg1,TiborKovács1,ZoltánKorsós2 & János Tor¨ ok¨ 1 1Behavioural Ecology Group, Department of Systematic Zoology and Ecology, E¨otv¨os Loránd University, Pázmány Péter sétány 1/C, H-1117 Budapest, Hungary; e-mail: [email protected] 2Department of Zoology, Hungarian Natural History Museum, Baross u. 13,H-1088 Budapest, Hungary Abstract: Microhabitat selection and seasonal activity of the snake-eyed skink, Ablephaus kitaibelii fitzingeri,arecompared to the two lacertid lizards (Lacerta viridis and Podarcis muralis) that co-occur in many of its habitats. The food composition of A. k. fitzingeri is also described. Significant differences in microhabitat selection and seasonal activity among the three species were found. The snake-eyed skink was associated with open grasslands, and with a low level of scrub, bare soil and rock cover. The microhabitat preference of L. viridis was quite similar to that of the skink, but with a higher preference for scrub. P. muralis occurred in places with greater rock and bare soil cover, and more scrub than A. k. fitzingeri. Activity of the snake-eyed skink decreased dramatically in summer, probably because of the reduced thermal inertia originating from the extremely small size of this species, but its seasonal activity overlapped with those of the lacertids. Stomach content analysis of the snake-eyed skink suggests that it is a generalist predator of small, mainly flightless arthropod prey. Competition with juvenile lacertids and predation by adult L. viridis are conceivable for the snake-eyed skink. Key words: Ablepharus kitaibelii fitzingeri; diet composition; Lacerta viridis; microhabitat use; Podarcis muralis;seasonal activity Introduction rent distribution and possible threatening factors of A. k. fitzingeri in Hungary was published recently (Herczeg The snake-eyed skink, Ablepharus kitaibelii Bibron et et al. 2004). Its general ecology is virtually unknown Bory, 1833 is the only representative of the genus in except from some anecdotal observations, and even its Europe and also the northernmost European represen- current demographic status is based on inadequate cen- tative of the family Scincidae. Despite the unique status sus data, and most local populations are subject to of the snake-eyed skink in the European herpetofauna, continued human disturbance (Korsós 1994; Herczeg & almost all aspects of its biology have remained unstud- Korsós 2003). Before any sound conservation plan can ied (Gasc et al. 1997; Pasuljevič 1965, 1976), proba- be developed, a basic knowledge of its general ecology bly because of its secretive habits. Ablepharus kitaibelii is required. fitzingeri Mertens, 1952, which occupies the northern Community structure and resource utilisation / range of the species’ distribution area, occurs mainly partition patterns of lizards have been an attrac- in Hungary, with sporadic records in southern Slovakia tive topic for ecologists in the last half century (e.g., and northern Serbia (Mertens 1952; Fuhn 1969; Gruber Schoener 1968; Pianka 1973; Vitt et al. 1981, 2000). 1981; Ljubisavljevic et al. 2002). From this work it was suggested that space, time and In Europe, the species is listed in the Bern Con- diet are perhaps the most important limiting factors vention (Council of Europe 1994), Appendix 2 and in where segregation in lizard assemblages could be de- the European Union Habitat Directive (European Com- tected (e.g., Schoener 1968; Pianka 1973; Toft 1985; mission 1992), Annex IV, as a species in need of strict Vrcibradic & Rocha 1996). The tools developed in these protection. A. k. fitzingeri is strictly protected in Hun- studies are widely used to answer conservation ques- gary and is listed in the Hungarian Red Data Book tions (e.g., Sartorius et al. 1999; Vega et al. 2000) or as a potentially endangered taxon (Rakonczay 1989). for describing the ecological requirements of endangered However, most previous studies have dealt only with species (e.g., Martín & Salvador 1995). In this paper, its morphology and distribution (e.g., Fitzinger 1829; we present the first report of microhabitat use, sea- Lendl 1899; Fejérváry 1912, 1917, 1925; Bolkay 1914; sonal activity and diet of the snake-eyed skink. With Méhely 1918; Fejérváry-Lángh 1943; Szunyoghy 1954; respect to microhabitat use and seasonal activity, we Dely 1978; Solti & Varga 1988). A summary of the cur- compared A. k. fitzingeri with the sympatric Lacerta c 2007 Institute of Zoology, Slovak Academy of Sciences Ecological notes on Ablepharus kitaibelii fitzingeri 483 viridis Laurenti, 1768 and Podarcis muralis Laurenti, the sample sizes were too small for biologically meaningful 1768, the lacertid lizards that co-occur with the snake- interpretations. Taxonomic diet composition was summa- eyed skink at most of its Hungarian sites (Herczeg & rized as the proportion of prey items from a given taxon Korsós 2003). Our goal was to provide some ecological in the total number of prey items (n%) and the proportion data on the snake-eyed skink, which conservationists of lizard individuals eating a prey taxon (F), after James (1991) and Maragou et al. (1996). can use for the conservation management of this reptile endemism of the Carpathian Basin. Statistical analyses We used principal components analysis to reduce the six Material and methods original environmental variables to a smaller number of or- thogonal principal components (PCs). We used data only from spring and autumn as A. k. fitzingeri was almost com- Study organisms and sampling pletely absent in summer (n = 2). Three PCs were extracted The northernmost subspecies (A. k. fitzingeri)ofthesnake- from the six original variables according to Kaiser’s criteria. eyed skink (A. kitaibelii) is one of the smallest lizards in To gather biologically interpretable PCs we rotated the ini- Europe, with a snout to vent length (SVL) of 20–55 mm tial factor solutions by the Varimax procedure. We tested (juveniles ca. 22–30 mm) and body mass (BM) of 0.15–1.5 for differences in the PC scores between species using Anal- g. In Hungary, it occurs in different habitats with respect ysis of Variance (ANOVA) followed by the LSD test. Due to substrate: sandstone, limestone, dolomite, andesite, gab- to the low number of observed A. k. fitzingeri individuals, bro, basalt, or even pure sand (Herczeg et al. 2004; for more we did not test for seasonal differences. We compared the details of the species see Gruber 1981). The common wall seasonal activities of the species using χ2 tests. lizard (P. muralis) is a rock-dwelling, insectivorous helio- We calculated Shannon diversity indices and compared therm species and has SVL of 25–65 mm (juveniles ca. 25–35 them with Hutcheson t-tests (Hutcheson 1970). To compare mm) and BM of 0.7–6.5 g, and is widespread in Europe (for the diet composition between the spring and autumn sam- details see Gruschwitz & B¨ohme 1986). The green lizard (L. ples, we calculated Proportional Similarity indices. To ex- viridis) is one of the largest lizards in Europe with SVL of plore the relationship between F and n%, we used the Spear- 30–120 mm (juveniles ca. 30–45 mm) and BM of 0.9–25 g. It man rank correlation test. is a ground-dwelling, insectivorous heliotherm lizard and is Because our purpose was to study interspecific differ- widespread in Europe (for details see Nettmann & Rykena ences, we randomly assigned individuals between sex, age 1984). and size categories. All statistics were computed using STA- Fieldwork was carried out in the Sas Hill Nature Re- TISTICA 7.0 for WINDOWS (StatSoft Inc., Tulsa, Okla- serve, a dolomite hill (maximum elevation 259 m a.s.l.) homa, 1994) software. within the area of Budapest (47◦30 N; 19◦51 E). The habi- tat offered various microhabitat types, such as closed or opened dolomite grasslands, solitary or aggregated scrub, Results forest patches and rocky outcrops. We sampled lizards over six, five and six days in spring, The three PCs together accounted for 75% of the total summer and autumn, respectively, from 12 March to 12 variance (Table 1). According to Norman & Streiner November in 2002 to investigate microhabitat use and sea- (2000), the critical value for the minimum acceptable sonal activity. Sampling days were once every second week factor loading was 0.362 in our case. The first PC was within each season and we chose mostly clear, sunny days. negatively correlated with cover and height of arbo- Sampling was always by the first author from 07.00 to 19.00 real plants and positively with the cover of herbaceous on each day. GH moved slowly through the area and if a lizard was detected, species and microhabitat variables plants (Table 1). Thus PC1 describes a gradient from (cover of herbaceous plants, cover of arboreal/mainly scrub/ grasslands to scrub and forest patches. The second PC plants, rock cover and percentage of bare soil were estimated was positively correlated with the cover and height of to the nearest 5%; height of herbaceous plants and arboreal herbaceous plants and negatively with rock cover (Ta- plants were measured (to the nearest 5 cm) and recorded ble 1), likewise describing a gradient from grassy areas within 2 m of the location where the lizard was first seen. A to rocky outcrops. The third PC was positively corre- constant effort was made to sample each habitat type. Al- lated with the cover of bare soil and negatively with the together 255 lizards (46 A. k. fitzingeri, 113 L. viridis,and cover of herbaceous plants (Table 1), i.e., it represents 96 P. muralis) were recorded. Some additional individuals a gradient from open, patchy grassland to thick, closed were observed without full data recording.

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